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JP3867454B2 - Membrane separation and purification equipment - Google Patents
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JP3867454B2 - Membrane separation and purification equipment - Google Patents

Membrane separation and purification equipment Download PDF

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JP3867454B2
JP3867454B2 JP30202199A JP30202199A JP3867454B2 JP 3867454 B2 JP3867454 B2 JP 3867454B2 JP 30202199 A JP30202199 A JP 30202199A JP 30202199 A JP30202199 A JP 30202199A JP 3867454 B2 JP3867454 B2 JP 3867454B2
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water
membrane
membrane separation
sludge
purification device
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JP2001121147A (en
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典英 佐保
哲也 田中
規世 西嶋
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Hitachi Ltd
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Hitachi Ltd
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Description

【0001】
【発明の属する技術分野】
本発明は、水質浄化や固液分離等を目的とした膜分離装置に関し、特に生物や汚濁有機物による膜目の閉塞を防止することのできる膜分離浄化装置に関する。
【0002】
【従来の技術】
固液分離等を目的として、細めの金膜や高分子繊維で編んだ膜を通水分離膜として粒子を膜で分離し除去する浄化装置がある。その例としては、 例えば化学技術誌MOL Vol.22, No.12 p47-51, (1984) に記載されているものなどがある。
【0003】
ステンレス鋼の細線、銅の細線、あるいはポリエステル繊維等で膜を構成し、被処理水は、例えばその数十ミクロンメートルの目開きを有した開口部を通過する。被処理水中の被処理物、例えばアオコ等の植物プランクトンや動物フランクトンや有機物等の汚濁物質はその投影面積や投影直径が開口部の投影面積や投影直径よりも大きい場合通過できず捕捉分離され、膜を透過した水は浄化水となる。このまま、同じ膜面に被処理水を通水し続けると、膜の通水側面に被処理物が堆積して通水抵抗が増大し、通水量が極端に低下し、浄化操作に支障をきたす。したがって、被処理水液面以下の部位にあるこの堆積物のある膜面を被処理水液面より上方の大気部まで移動させ、例えばシャワー状の浄化水を使用して膜を洗浄し、その洗浄水と堆積物の混合水をスラッジとして分離部系から排除し、膜面を洗浄再生し再び被処理水液面以下の部位に戻す構造としている。シャワー水で洗浄しきれなかった少量のアオコ等の植物プランクトン、動物プランクトン、微小動物の幼虫や卵、有機物等の汚濁物質は膜の表面に残留する。
【0004】
スラッジは最終的には、通常トラックで処分場や焼却場に運搬したり、コンポスト化する。
【0005】
【発明が解決しようとする課題】
上記のように、従来例では、シャワー水で洗浄しきれなかった少量のアオコ等の植物プランクトン、動物プランクトン、微小動物の幼虫や卵、有機物等の汚濁物質が膜の表面に残留し、これらの生物が繁殖して膜に固着するとシャワー水で除去できなくなり、膜目が閉塞したり目が狭くなって通水量が減少し、浄化性能を低下させる問題があった。
【0006】
本発明の目的は、特に生物や汚濁有機物による膜目の閉塞を防止できる膜分離浄化装置を得ることにある。
【0007】
【課題を解決するための手段】
上記目的は、被除去物を含む被処理流体あるいは被除去物を含む流体に、被除去物より密度が大きいシーディング材と凝集剤を添加することにより前記被除去物と前記シーディング材を含むフロックを生成する手段と、このフロックの生成された被処理流体を濾過するものであって、被除去物やフロックが通過できない目開きを有する網からなる濾過手段と、この濾過手段の表面に捕捉された被除去物やフロック等の堆積物を被処理流体の液面より上方に移動させ、この堆積物を前記濾過手段の表面から水流力で剥離させるための洗浄手段とを備えた膜分離浄化装置において、前記濾過手段の濾過面の内外面を照射して殺菌する紫外線を設けたことにより達成される。
【0008】
ここで、前記濾過手段を網状細線で構成し、この網状細線表面に光触媒を固定化すると更に良い。
【0009】
すなわち、本発明では、例えば、シャワー状の浄化水を使用して膜を洗浄した後、膜表面に紫外線を照射する紫外線発生ランプを配置する。また、ステンレス鋼の細線や銅の細線の表面に酸化チタンの粒子を結合したり膜をコーティングし、紫外線をこの表面に照射し、その表面に活性酸素を発生させるようにしたものである。
【0010】
この紫外線照射による殺菌作用により、シャワー水で洗浄しきれなかった少量のアオコ等の植物プランクトン、動物フランクトン、微小動物の幼虫や卵等は死滅し、その後増殖することはなく、活性酸素により残存汚濁有機物とともに酸化分解され、その後のシャワー水で洗浄される。したがって、膜目が閉塞したり目が狭くなって通水量が減少することがなく、浄化性能を長期間にわたって維持できる膜分離浄化装置が得られる。
【0011】
【発明の実施の形態】
以下、本発明の一実施例を図1、図2及び図3により説明する。図2は図1の膜分離浄化装置8の拡大断面図、図3は図2の上部から見た半断面図である。被処理水である原水を,水源例えば貯水池1から、導管2、大きなゴミを取るためのフィルタ3を通してポンプ4で原水貯槽5に汲み上げ,この原水6を配管7を通して膜分離浄化装置8に流入させる。
【0012】
図2、図3により膜分離浄化装置の構造を説明する。ステンレス鋼の細線や銅の細線やポリエステル繊維等で数ミクロンメートルから数十ミクロンメートルの目開きを有した開口部を有する膜9をドラム状に構成し、膜9の両端は目開きのないドラム状のシェル10,11に接合され、その一方向はフランジ12に接合されて一体化され、フランジ12の中央部はロッド13に接合されロッド13がモータ14で回転することにより、フランジ12、シェル10、ドラム状の膜9、シェル11が回転する。シェル11と固定フランジ15は摺動面16で気密性を維持しながら回転摺動する。膜9の外側に浄化水槽17を配置する。原水6は導管7からドラム状の膜9内に流入し、原水6は膜9を通過する。この時原水6中の被除去物18は膜9内面に捕捉され、膜9を通過し被除去物18を分離された水は浄化水19となって浄化水槽17に溜り、配管20を通って貯水池1に放流される。原水6が膜9を通水する動力は原水6と浄化水19との液面位差である。一方、被除去物18は図2で反時計回りに回転する膜9内面に通水抵抗によって付着し堆積物となって液面上の大気部に露出する。
【0013】
露出した被除去物18の堆積物は、即通水の障害にはならないが、長時間運転して堆積物が増加すると通水の障害となる。浄化水槽17内の浄化水をポンプ21の取水口22から吸い込み導管23からシャワー管24に送り、孔からシャワー水25を、膜9外表面から内面側に吹き付ける。膜9の内表面に蓄積した堆積物はシャワー水で剥がれ膜9面は再生され、内側に設けたトレイ26に堆積物を含む洗浄水は溜る。この洗浄水は、排水口27から流失し、配管28を通ってスラッジタンク29に溜まる。
【0014】
洗浄された膜9の内外面には、原水内の微生物等が付着し繁殖し、膜9の目を閉塞する虞がある。これを防ぐため本実施例では、紫外線ランプ30,31を保護ガラス管32,33に挿入して配置する。保護ガラス管32,33の内面にはそれぞれ上半分と下半分の部分にアルミニュウム蒸着膜を付着させ、紫外線が反射して、膜9の内外面に紫外線が照射されるようにする。膜9に付着した動・植物プランクトン生物の卵や幼虫が紫外線で死滅することにより網上で繁殖することがなくなり、膜9の目を閉塞したり狭くしたりして浄化機能に障害を与えることを防止できる。また、膜9を構成する細線や繊維上に酸化チタン等の活性酸化触媒物質を固定化することにより、紫外線照射により活性酸素を発生させることができる。この活性酸素により、膜9に付着する有機物を酸化分解して、膜9の有機物等の汚れを取り除くことができる。
【0015】
スラッジタンク29に溜まったスラッジは、配管34を通じて遠心分離機やベルトプレス機等の脱水設備35により濃縮された後、堆肥等に処理される。
【0016】
なお、本実施例では膜9をドラム状に形成した場合について説明したが、膜9をディスク状に構成し、このディスクを縦方向に複数枚配置して浄化装置を構成しても、膜の内外面に紫外線を照射して同様な膜分離浄化装置が得られる。
【0017】
図4に本発明の他の実施例を示す。図1の実施例と異なる点は、原水6に密度が大きい無機質物等の砂粒子や粉砕ガラス粒子のシーディング材を添加するためのシーディング添加装置36及び配管37を備えていること、またpH調整剤、ポリ塩化アルミニウム等の凝集剤や高分子補強剤等を加えるための薬剤添加装置38及び配管39を備えていること、原水とこれらの添加物を攪拌するための撹絆槽40と攪拌翼42を回転駆動するモータ41を備えていることである。これによって、数百ミクロンメートル〜数ミリメートル程度の大きさの被除去物とシーディング材を含み、密度を大きくされたフロックを多量に含む前処理水43が生成される。この前処理水43を導管7を通じて膜分離浄化装置8に通水する。
【0018】
膜9で分離されたフロックをシャワー水25で洗浄し、フロックを含む洗浄水をトレイ26で回収する点は図2、図3で説明した実施例と同様であるが、本実施例の場合、密度が小さい被除去物単体を洗浄する前記の場合に比べ、フロックの体積と密度が大きいため、洗浄時にその重力とシャワー水をフロック表面に蓄えられその重力が作用して、より少ないシャワー水量で容易に膜9から剥離させ、スラッジを回収することができる。したがって、本実施例では、スラッジの含水率が小さく高濃縮のスラッジを得ることができる。したがって、後段側の遠心分離機等の脱水手段の処理能力が小さくて済み、装置コスト、運転コストを低減できる効果がある。また、本実施例では、膜9からフロックの剥離のためにシャワー水を使用したが、シャワー水の代わりに空気圧縮機により圧搾空気をシャワー管24から高圧空気シャワーとして放射しても密度の高いフロックは容易に剥離され、膜9を洗浄することができる。この場合、洗浄に水を使用しないので、剥離したフロックの含水率を更に低くして高濃縮のスラッジを得ることができる。したがって、後段側の遠心分離機等の脱水手段の処理能力を小さくでき、装置コストや運転コストを低減することができる。
【0019】
回収されたスラッジを熱分解し、スラッジの減容化及びシーディング材の回収再利用のため、スラッジはスラッジタンク29から配管44及びスラリ加圧ポンプ45を介して下流側に送られる。スラリ加圧ポンプ45入り口部で、薬剤タンク46から、高温高圧水で処理する際必要な水、反応促進剤及び中和剤のアルカリ溶液等を弁47を通してスラッジに添加される。
【0020】
スラリ加圧ポンプ45で2MPa程度に加圧されたスラッジは、反応管48内に吐出され、処理後の熱回収用の予熱熱交換器49で予熱され、ヒータ等を内蔵した温度調節器50で温度が200度の亜臨界状態にされる。
【0021】
ここで、スラッジ中の被除去物である植物や動物プランクトン等は有機物であり、凝集剤としては無機系、有機系がある。したがって、亜臨界水中では凝集したフロックやはその結合が破壊され、フロック中の固形物がバラバラになり、有機物は油状の粘性の高い液体と水分が混在した亜臨界溶液となり、スラッジ中のシーディング材の周りから凝集剤が剥がれ、シーディング材単体で分離する。したがって、シーディング材分離器51では回転流によるサイクロン作用等で密度の高いシーディング材は側壁側から沈降し下部に溜まる。ある程度シーディング材が蓄積すると、弁52を開いて内圧を利用してシーディング材スラリを回収槽53に回収する。回収したシーディング材は再利用する。
【0022】
スラッジはシーディング材分離器51を出た後、薬剤タンク54から、高温高圧水中で酸化処理する際に必要な、酸素、過酸化水素水、空気、共晶反応剤、アルカリ溶液等を、弁55を介して、ヒータを内臓した反応管56内のスラッジに添加される。反応管56で温度管理されたスラッジは反応管56内で、スラッジ中に含まれる有機物が酸化され減容化され、スラッジ中に存在するリンは化学反応によってリン酸塩となって固形沈殿物となる。反応管56のラインには安全弁57を取り付けている。
【0023】
その後、高温高圧スラッジ溶液は、配管58を通り、予熱熱交換器49で熱が回収され、フラッシュタンク59内から圧力調整弁60を介して減圧、噴霧される。フラッシュタンク59内は圧力調整弁60で大気圧より若干高い圧力に調整される。ここで、高温・高圧スラッジ溶液中の水分の一部は内部熱容量で自己蒸発し、残りは内蔵したヒータ等で加熱されて蒸発し、蒸発した蒸気はフラッシュタンクを保温し、圧力調整弁61から放出される。フラッシュタンク59内でスラッジ中の未酸化有機物や無機物分子は乾燥固形化され、容器底部に乾燥物が沈降分離されタンク外に取り出され、溶液分は、配管62や流量調整弁63を介して導かれた原水と配管64で混合され、水質を調整された後、下水や植生設備等に放流される。
【0024】
本実施例では、高温高圧水では凝集剤の凝集作用が壊れ、フロック中の固形物がバラバラになり、スラッジ中のシーディング材の周りから凝集剤が剥がれ、シーディング材単体で分離できるので再使用する際、純度の高いシーディング材を回収することができる。遠心分離機やベルトプレス機等の濃縮手段を使用せずにスラッジを処理できるので装置コストが低減でき、また、スラッジは減容化されるのでスラッジ処理コストも低減できる。
【0025】
なお、本実施例では、凝集剤を使用せず、被除去物を含むフロックを生成しないでシーディング材と被除去物との混合物を膜分離する場合にも適用でき、シーディング材を回収・再利用することができる。
【0026】
また、被除去物とほぼ同じサイズもしくは被除去物より小さくかつ膜で捕捉されるサイズのシーディング材を原水中に注入して混合し、被除去物をシーディング材との混合物として膜表面に捕捉堆積させ、この密度の大きい混合物を少ないシャワー水量で膜からシャワー水の水圧及び重力で剥離させるようにすれば、凝集剤を使用することなく同様な効果を生じさせることができる。
【0027】
なお、本実施例では紫外線ランプを殺菌手段として用いたが、電磁波照射や電気通電による殺菌処理でも同様な効果が得られる。
【0028】
また、保護ガラス管32,33の外表面の汚れを洗浄するために、浄化水を洗浄水として使用し連続的もしくは周期的に、外表面を機械的なブラシやワイパー等で、もしくは洗浄流水で汚れを剥離除去する洗浄手段を設ければ、紫外線の殺菌効率を維持することができる。この場合、機械的なブラシ、ワイパー、洗浄水吹き出し孔を固定し、保護ガラス管32,33を洗浄中に回転させながら外表面の全周を洗浄する構成とすることもできる。
【0029】
【発明の効果】
本発明によれば、紫外線照射などの殺菌手段を設けているから、その殺菌作用により、シャワー水で洗浄仕切れなかった少量のアオコ等の植物プランクトン、動物プランクトンや微小動物の幼虫や卵を死滅させることができ、その増殖を防止できるから、活性酸素により残存汚濁有機物と共に酸化分解して、その後のシャワー水等で洗浄除去することができる。したがって、膜目が閉塞したり目が狭くなって通水量が減少するのを防止でき、浄化性能を長期間にわたり維持できる膜分離浄化装置を得ることができる効果がある。
【図面の簡単な説明】
【図1】本発明の一実施例を示す膜分離浄化装置の系統図。
【図2】図1に示す膜分離浄化装置の縦断面図。
【図3】図2の膜分離浄化装置を一部断面で示した平面図。
【図4】本発明の他の実施例を示す膜分離浄化装置の系統図。
【符号の説明】
6…原水、9…膜、17…浄化水槽、18…被除去物、19…浄化水、25…シャワー水、30,31…紫外線ランプ、 32,33…保護ガラス管。
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a membrane separation device for the purpose of water purification, solid-liquid separation, and the like, and more particularly to a membrane separation and purification device capable of preventing clogging of membranes by living organisms and contaminated organic substances.
[0002]
[Prior art]
For the purpose of solid-liquid separation and the like, there is a purification device that separates and removes particles with a thin water membrane or a membrane knitted with polymer fibers as a water separation membrane. Examples thereof include those described in the chemical technical journal MOL Vol.22, No.12 p47-51, (1984).
[0003]
A membrane is formed of stainless steel fine wire, copper fine wire, polyester fiber, or the like, and the water to be treated passes through an opening having an opening of, for example, several tens of micrometers. Objects to be treated in the treated water, such as phytoplankton such as blue sea bream, animal frankton, organic matter, and other contaminants cannot be passed and captured and separated if the projected area or projected diameter is larger than the projected area or projected diameter of the opening. The water that has passed through the membrane becomes purified water. If the water to be treated continues to flow through the same membrane surface, the material to be treated accumulates on the water flow side surface of the membrane, the water flow resistance increases, the water flow rate decreases extremely, and the purification operation is hindered. . Therefore, the film surface with the deposit in the portion below the surface of the water to be treated is moved to the atmosphere above the surface of the water to be treated, and the film is washed using, for example, shower-like purified water. The mixed water of the cleaning water and the sediment is removed from the separation unit system as sludge, and the membrane surface is cleaned and regenerated and returned to the portion below the liquid surface to be treated. A small amount of phytoplankton, zooplankton, zooplankton, tiny animal larvae and eggs, organic matter, etc. that could not be washed with shower water remain on the surface of the membrane.
[0004]
Ultimately, the sludge is usually transported to a disposal site or incinerator by a truck or composted.
[0005]
[Problems to be solved by the invention]
As described above, in the conventional example, a small amount of phytoplankton such as aquatic, zooplankton, minute animal larvae and eggs, organic matter, etc. that could not be washed with shower water remained on the surface of the membrane. When organisms propagate and stick to the membrane, they cannot be removed with shower water, and the membrane is clogged or narrowed to reduce the amount of water flow, thus degrading the purification performance.
[0006]
An object of the present invention is to obtain a membrane separation and purification device that can prevent clogging of membranes caused by organisms and polluted organic substances.
[0007]
[Means for Solving the Problems]
The object includes the object to be removed and the seeding material by adding a seeding material and a flocculant having a higher density than the object to be removed to the fluid to be treated or the fluid containing the object to be removed. A means for generating flocs, a fluid to be treated in which the flocs are generated is filtered, and a filtering means comprising a mesh having an opening through which an object to be removed or floc cannot pass, and captured on the surface of the filtering means The membrane separation purification provided with cleaning means for moving the deposits such as the removal object and flocks above the liquid level of the fluid to be treated and separating the deposits from the surface of the filtering means by a hydrodynamic force In the apparatus, this is achieved by providing ultraviolet light that irradiates and sterilizes the inner and outer surfaces of the filtering surface of the filtering means.
[0008]
Here, it is further preferable that the filtering means is constituted by a fine mesh wire, and the photocatalyst is immobilized on the surface of the fine mesh wire.
[0009]
That is, in the present invention, for example, after the film is washed using shower-like purified water, an ultraviolet ray generating lamp that irradiates the film surface with ultraviolet rays is disposed. In addition, titanium oxide particles or a film is coated on the surface of a stainless steel fine wire or a copper fine wire, and the surface is irradiated with ultraviolet rays to generate active oxygen on the surface.
[0010]
Due to this germicidal action by UV irradiation, a small amount of phytoplankton such as sea cucumbers, animal flanks, larvae and eggs of minute animals that could not be washed with shower water will die and will not proliferate and remain with active oxygen. It is oxidatively decomposed with contaminated organic matter and then washed with shower water. Therefore, there is obtained a membrane separation and purification device capable of maintaining the purification performance over a long period of time without clogging or narrowing the membrane and reducing the amount of water flow.
[0011]
DETAILED DESCRIPTION OF THE INVENTION
An embodiment of the present invention will be described below with reference to FIGS. 2 is an enlarged cross-sectional view of the membrane separation and purification device 8 of FIG. 1, and FIG. 3 is a half cross-sectional view as seen from the top of FIG. Raw water, which is to be treated, is pumped from a water source, for example, a reservoir 1 to a raw water storage tank 5 by a pump 4 through a conduit 2 and a filter 3 for removing large garbage, and this raw water 6 flows into a membrane separation and purification device 8 through a pipe 7. .
[0012]
The structure of the membrane separation and purification device will be described with reference to FIGS. A film 9 having an opening having an opening of several to several tens of micrometers made of stainless steel fine wire, copper fine wire, polyester fiber or the like is formed in a drum shape, and both ends of the film 9 are drums having no openings. Are joined to the flange 12 in one direction, and the flange 12 is joined to and integrated with the rod 12, and the center of the flange 12 is joined to the rod 13 and the rod 13 is rotated by the motor 14. 10. Drum-like film 9 and shell 11 rotate. The shell 11 and the fixed flange 15 are slidably rotated while maintaining airtightness on the sliding surface 16. A purified water tank 17 is disposed outside the membrane 9. The raw water 6 flows from the conduit 7 into the drum-shaped membrane 9, and the raw water 6 passes through the membrane 9. At this time, the object to be removed 18 in the raw water 6 is captured by the inner surface of the membrane 9, and the water that has passed through the membrane 9 and separated from the object to be removed 18 becomes purified water 19 and accumulates in the purified water tank 17 and passes through the pipe 20. Released into reservoir 1. The power that the raw water 6 passes through the membrane 9 is the liquid level difference between the raw water 6 and the purified water 19. On the other hand, the object 18 to be removed adheres to the inner surface of the film 9 rotating counterclockwise in FIG.
[0013]
The exposed deposit 18 to be removed does not immediately impede water flow. However, when the deposit increases after a long period of operation, it impedes water flow. Purified water in the purified water tank 17 is sucked from the water intake port 22 of the pump 21 and sent from the conduit 23 to the shower tube 24, and shower water 25 is blown from the hole to the inner surface side from the outer surface of the membrane 9. Deposits accumulated on the inner surface of the film 9 are peeled off by shower water, the surface of the film 9 is regenerated, and cleaning water containing the deposits accumulates in a tray 26 provided inside. The washing water flows away from the drain port 27 and accumulates in the sludge tank 29 through the pipe 28.
[0014]
There is a possibility that microorganisms or the like in the raw water adhere to and propagate on the inner and outer surfaces of the washed membrane 9 and block the eyes of the membrane 9. In order to prevent this, in this embodiment, the ultraviolet lamps 30 and 31 are inserted into the protective glass tubes 32 and 33 and arranged. On the inner surfaces of the protective glass tubes 32 and 33, an aluminum vapor deposition film is attached to the upper half and the lower half, respectively, so that the ultraviolet rays are reflected and the inner and outer surfaces of the film 9 are irradiated with the ultraviolet rays. Eggs and larvae of animal and phytoplankton organisms attached to the membrane 9 do not propagate on the net by being killed by ultraviolet rays, and the membrane 9 is closed or narrowed to impair the purification function. Can be prevented. Further, by immobilizing an active oxidation catalyst material such as titanium oxide on the fine wires and fibers constituting the membrane 9, active oxygen can be generated by irradiation with ultraviolet rays. With this active oxygen, organic matter adhering to the film 9 can be oxidatively decomposed to remove dirt such as organic matter on the film 9.
[0015]
The sludge accumulated in the sludge tank 29 is concentrated by a dehydration facility 35 such as a centrifuge or a belt press through a pipe 34 and then processed into compost or the like.
[0016]
In this embodiment, the case where the film 9 is formed in a drum shape has been described. However, even if the film 9 is configured in a disk shape and a plurality of the disks are arranged in the vertical direction to configure the purification device, A similar membrane separation and purification device can be obtained by irradiating the inner and outer surfaces with ultraviolet rays.
[0017]
FIG. 4 shows another embodiment of the present invention. The difference from the embodiment of FIG. 1 is that the raw water 6 is provided with a seeding addition device 36 and a pipe 37 for adding a seed material of sand particles such as minerals having a high density or crushed glass particles. a pH adjusting agent, a chemical addition device 38 for adding a flocculant such as polyaluminum chloride and a polymer reinforcing agent, and a pipe 39; a stirring tank 40 for stirring the raw water and these additives; The motor 41 that rotationally drives the stirring blade 42 is provided. As a result, the pretreated water 43 containing a large amount of flocs having a large density is generated, which includes the object to be removed and the seeding material having a size of several hundred microns to several millimeters. The pretreated water 43 is passed through the conduit 7 to the membrane separation and purification device 8.
[0018]
The point that the floc separated by the membrane 9 is washed with the shower water 25 and the washing water containing the floc is collected by the tray 26 is the same as the embodiment described with reference to FIGS. 2 and 3, but in this embodiment, Compared to the case where the object to be removed having a low density is washed, since the volume and density of the floc are large, the gravity and shower water are stored on the floc surface during washing, and the gravity acts to reduce the amount of shower water. It can be easily peeled off from the membrane 9 and sludge can be recovered. Therefore, in this embodiment, a highly concentrated sludge having a small moisture content in the sludge can be obtained. Therefore, the processing capacity of the dewatering means such as the centrifuge at the rear stage is small, and there is an effect that the apparatus cost and the operation cost can be reduced. Further, in this embodiment, shower water is used for peeling flocs from the membrane 9, but the density is high even if compressed air is emitted from the shower tube 24 as a high-pressure air shower by an air compressor instead of shower water. The floc is easily peeled off and the membrane 9 can be cleaned. In this case, since water is not used for washing, the moisture content of the flocs peeled off can be further reduced to obtain highly concentrated sludge. Therefore, it is possible to reduce the processing capacity of the dehydrating means such as the centrifuge on the rear stage side, and to reduce the apparatus cost and the operating cost.
[0019]
The recovered sludge is pyrolyzed, and the sludge is sent to the downstream side from the sludge tank 29 via the pipe 44 and the slurry pressurizing pump 45 in order to reduce the sludge volume and recover and reuse the seeding material. At the inlet of the slurry pressurizing pump 45, water necessary for processing with high-temperature and high-pressure water, an alkali solution of a reaction accelerator and a neutralizing agent, etc. are added to the sludge through the valve 47 from the chemical tank 46.
[0020]
The sludge pressurized to about 2 MPa by the slurry pressurizing pump 45 is discharged into the reaction tube 48, preheated by the preheating heat exchanger 49 for heat recovery after the treatment, and by the temperature controller 50 incorporating a heater or the like. The temperature is brought to a subcritical state of 200 degrees.
[0021]
Here, plants, zooplankton, and the like, which are objects to be removed in the sludge, are organic substances, and there are inorganic and organic flocculants. Therefore, the aggregates of flocs and aggregates in subcritical water are broken, the solids in the flocs fall apart, and the organic matter becomes a subcritical solution with a mixture of oily viscous liquid and moisture, and seeding in sludge The flocculant is peeled off around the material and separated by the seeding material alone. Accordingly, in the seeding material separator 51, a high density seeding material settles from the side wall side and accumulates in the lower part due to a cyclone action by a rotating flow. When the seeding material accumulates to some extent, the valve 52 is opened and the seeding material slurry is recovered in the recovery tank 53 using the internal pressure. The recovered seeding material is reused.
[0022]
After the sludge exits the seeding material separator 51, the oxygen, hydrogen peroxide solution, air, eutectic reagent, alkaline solution, etc. necessary for the oxidation treatment in the high-temperature high-pressure water are supplied from the chemical tank 54 to the valve. Through 55, it is added to the sludge in the reaction tube 56 with a built-in heater. The sludge whose temperature is controlled in the reaction tube 56 is oxidized in the reaction tube 56 to reduce the volume of organic substances contained in the sludge, and the phosphorus present in the sludge is converted into phosphate by a chemical reaction to form a solid precipitate. Become. A safety valve 57 is attached to the line of the reaction tube 56.
[0023]
Thereafter, the high-temperature and high-pressure sludge solution passes through the pipe 58, recovers heat by the preheating heat exchanger 49, and is depressurized and sprayed from the flash tank 59 through the pressure regulating valve 60. The inside of the flash tank 59 is adjusted to a pressure slightly higher than the atmospheric pressure by the pressure adjusting valve 60. Here, a part of the water in the high-temperature / high-pressure sludge solution is self-evaporated by the internal heat capacity, and the rest is heated and evaporated by a built-in heater or the like, and the evaporated vapor keeps the flash tank warm, and from the pressure regulating valve 61 Released. In the flash tank 59, the unoxidized organic matter and inorganic molecules in the sludge are dried and solidified, and the dried matter is settled and separated at the bottom of the container and taken out of the tank. The solution is introduced via the pipe 62 and the flow rate adjusting valve 63. The raw water is mixed with the pipe 64 and the water quality is adjusted, and then discharged into sewage and vegetation facilities.
[0024]
In this example, the flocculating action of the flocculant is broken in high-temperature and high-pressure water, the solid matter in the floc is broken, the flocculant is peeled off from around the seeding material in the sludge, and can be separated by the seeding material alone. When used, a high-purity seeding material can be recovered. Since sludge can be processed without using a concentrating means such as a centrifugal separator or a belt press machine, the apparatus cost can be reduced, and the sludge volume can be reduced, so that the sludge treatment cost can also be reduced.
[0025]
In this embodiment, the present invention can also be applied to a case where a mixture of a seeding material and a material to be removed is not separated without using a flocculant and without generating a floc containing the material to be removed. Can be reused.
[0026]
In addition, a seeding material of approximately the same size as the object to be removed or smaller than the object to be removed and captured by the membrane is poured into the raw water and mixed, and the object to be removed is mixed with the seeding material on the membrane surface. The same effect can be produced without using an aggregating agent by trapping and depositing the mixture having a high density so as to be peeled off from the film by the water pressure and gravity of the shower water with a small amount of shower water.
[0027]
In the present embodiment, an ultraviolet lamp is used as the sterilizing means, but the same effect can be obtained by sterilization treatment by electromagnetic wave irradiation or electrical conduction.
[0028]
Further, in order to clean dirt on the outer surfaces of the protective glass tubes 32 and 33, purified water is used as cleaning water, and the outer surface is mechanically brushed or wiped or continuously or periodically with cleaning water. If cleaning means for peeling off and removing dirt is provided, the sterilization efficiency of ultraviolet rays can be maintained. In this case, a mechanical brush, a wiper, and a washing water blowing hole may be fixed, and the entire circumference of the outer surface may be washed while rotating the protective glass tubes 32 and 33 during washing.
[0029]
【The invention's effect】
According to the present invention, since sterilizing means such as ultraviolet irradiation is provided, the sterilizing action kills a small amount of phytoplankton such as sea cucumber, zooplankton and tiny animal larvae and eggs that were not washed and partitioned with shower water. Since the growth can be prevented, it can be oxidatively decomposed together with the remaining polluted organic matter with active oxygen and then washed away with shower water or the like. Therefore, there is an effect that it is possible to prevent the membrane from being clogged or the eyes from becoming narrow and to reduce the amount of water flow, and to obtain a membrane separation and purification device capable of maintaining the purification performance for a long period of time.
[Brief description of the drawings]
FIG. 1 is a system diagram of a membrane separation and purification device showing an embodiment of the present invention.
FIG. 2 is a longitudinal sectional view of the membrane separation and purification device shown in FIG.
3 is a plan view showing a partial cross section of the membrane separation and purification device of FIG. 2; FIG.
FIG. 4 is a system diagram of a membrane separation and purification device showing another embodiment of the present invention.
[Explanation of symbols]
6 ... Raw water, 9 ... Membrane, 17 ... Purified water tank, 18 ... Objects to be removed, 19 ... Purified water, 25 ... Shower water, 30, 31 ... UV lamp, 32, 33 ... Protective glass tube.

Claims (2)

被除去物を含む被処理流体あるいは被除去物を含む流体に、被除去物より密度が大きいシーディング材と凝集剤を添加することにより前記被除去物と前記シーディング材を含むフロックを生成する手段と、このフロックの生成された被処理流体を濾過するものであって、被除去物やフロックが通過できない目開きを有する網からなる濾過手段と、この濾過手段の表面に捕捉された被除去物やフロック等の堆積物を被処理流体の液面より上方に移動させ、この堆積物を前記濾過手段の表面から水流力で剥離させるための洗浄手段とを備えた膜分離浄化装置において、
前記濾過手段の濾過面の内外面を照射して殺菌する紫外線を設けたことを特徴とする膜分離浄化装置。
A floc containing the to-be-removed object and the seeding material is generated by adding a seeding material and a flocculant having a density higher than that of the to-be-removed object to the fluid to be treated or the fluid containing the to-be-removed object. Means for filtering the fluid to be processed in which the flocs are generated, the filtering means comprising a mesh having an opening through which the object to be removed and the floc cannot pass, and the removal target captured on the surface of the filtering means In a membrane separation and purification apparatus comprising a cleaning means for moving deposits such as deposits and flocks above the liquid level of the fluid to be treated, and separating the deposits from the surface of the filtering means by water flow force ,
An apparatus for separating and purifying membranes, characterized in that ultraviolet rays that sterilize by irradiating the inner and outer surfaces of the filtration surface of the filtration means are provided .
請求項1記載の膜分離浄化装置において、
前記洗浄手段は、前記濾過手段によって浄化された浄化水を吸い上げるポンプとシャワー管とからなることを特徴とする膜分離浄化装置。
The membrane separation and purification device according to claim 1,
The membrane separation and purification device , wherein the cleaning means comprises a pump that sucks up the purified water purified by the filtering means and a shower tube .
JP30202199A 1999-10-25 1999-10-25 Membrane separation and purification equipment Expired - Fee Related JP3867454B2 (en)

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KR20040005486A (en) * 2002-07-10 2004-01-16 김종목 Sludge purification apparatus
KR100454069B1 (en) * 2002-09-25 2004-10-26 한국바이오시스템(주) Pre-treatment system equipped with UV sterilization lamps for the removal of suspended solids and biofilm in wastewater
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CN104150630B (en) * 2014-08-20 2016-04-06 郑州银科尔科技有限公司 A kind of heavy metal chelating machine
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